Person: Feibicke, Michael
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Veröffentlichung Fate, bioaccumulation and toxic effects of triclosan on a freshwater community - a mesocosm study(2021) Berghahn, Rüdiger; Contardo-Jara, Valeska; Feibicke, Michael; Meinecke, Stefan; Mohr, Silvia; Schmidt, RalfThe antibacterial agent triclosan (TCS) is added to many daily-used consumer products and can therefore reach the aquatic environment via treated wastewater and potentially harm aquatic ecosystems. A 120 days pond mesocosm study was conducted in order to investigate the fate of TCS in water and sediment, its bioaccumulative potential in different biota as well as the effects of TCS and its main transformation product methyl-triclosan (M-TCS) on plankton, periphyton, macrophytes, and benthos communities. TCS was dosed once each in six pond mesocosms (nominal concentrations: 0.12, 0.6, 3.5, 21, 130 and 778 (micro)g/L TCS, respectively) while two ponds served as controls. A concentration-dependent increase in the DT50 values from 5.0 to 15.0 and 7.5 to 16.3 days was observed for TCS in water and the whole pond system (water, sediment, biota), respectively. Consequently, the substance should be categorized as non-persistent. For TCS, the bioaccumulation factors (non steady-state conditions, BAFnssc) in Lymnaea stagnalis, Myriophyllum spicatum and periphyton were below the critical limit of 2000, above which a substance is classified as bioaccumulative. In contrast, a BAFnssc value of >10,000 was found for M-TCS in L. stagnalis, denoting that M-TCS definitely falls under this classification. Although strong effects on freshwater communities could only be observed in the highest TCS treatments, some periphyton species, such as Oedogonium spp., reacted very sensitive to TCS with an EC50 (time weighted average, 28 d) of 0.3 (micro)g/L TCS. Considering the high bioaccumulative potential of M-TCS in combination with the observed effects of TCS at low doses suggests that the use of TCS, and therefore its release into the environment, should cease. © 2021 The AuthorsVeröffentlichung Effects of copper ions on non-target species: a case study using the Grazer Theodoxus fluviatilis (Gastropoda: Neritidae)(2020) Rothmeier, Louisa Marie; Feibicke, Michael; Martens, Andreas; Gergs, René; Watermann, Burkard; Kullwatz, Jan Christopher; Sahm, RenéThe heavy metal copper has been widely used in industrial processes as well as a pesticide product in agriculture or as biocide. Anthropogenic activities by which copper can enter the environment are rather diverse including mining, metal finishing factories, discharging in industry, or sewage treatment plants. In agriculture, copper compounds are used mainly as fungicides or herbicides (e.g. reviewed by Flemming and Trevors 1989). Furthermore, it was formerly used in reservoirs, streams and ponds for controlling algae blooms and is now commonly used as a biocide in antifouling paintings for ships to protect hulls from corrosion and for fuel efficiency (Piola et al. 2009; Watermann et al. 2017). When copper is released into freshwater systems, for example via agricultural runoff, it exists in surface waters in the form of free ions (Cu2+), complexed with ligands or bound to particles, occurring at median water concentrations often ranging between 4 to 10 Ìg Cu2+/L (ATSDR 2004). As a persistent element, copper is able to accumulate in biofilms (Morin et al. 2008) and sediments of rivers, lakes and estuaries, from where it can also be remobilised (Watermann et al. 2017). Absorption of copper ions into biofilms increases with increasing ion concentration (Bhaskar and Bhosle 2006), leading to highly contaminated biofilms in polluted environments. © 2020 Springer Nature Switzerland AG